林业科学 ›› 2026, Vol. 62 ›› Issue (1): 42-56.doi: 10.11707/j.1001-7488.LYKX20250296
收稿日期:2025-05-09
修回日期:2025-11-09
出版日期:2026-01-25
发布日期:2026-01-14
通讯作者:
苏建荣
E-mail:jianrongsu@vip.sina.com
基金资助:
Jiao Liu1,2,Aixia Yang3,Shuaifeng Li1,Jianrong Su1,*(
)
Received:2025-05-09
Revised:2025-11-09
Online:2026-01-25
Published:2026-01-14
Contact:
Jianrong Su
E-mail:jianrongsu@vip.sina.com
摘要:
目的: 构建生态系统健康评估框架与综合阻力面,识别川滇生态屏障区生态源地和关键节点,为研究区生态安全格局优化奠定基础,为生态保护与修复提供科学依据。方法: 基于2021年多源基础数据和“生态活力?组织力?恢复力?生态系统服务”框架,利用InVEST、Fragstats和TerrSet等软件,评估研究区生态系统健康空间分布,确定最优生态源保护方案;采用随机森林模型计算未来土地利用发展概率,结合自然和社会因子构建综合生态阻力面,应用电路理论模型构建研究区生态安全格局。结果: 2021年,研究区生态系统物理健康指数、活力、组织力和恢复力均呈现明显的空间分异。生态系统物理健康指数和活力平均值分别为0.533和0.546,呈南高北低分布,高值区主要分布在生态系统类型多样、野生生物资源丰富、植被覆盖率较高及水资源充足的南部、西南部、中部和北部;西北部和东部的生态系统物理健康和活力水平较低。组织力平均值为0.583,受地形阻隔影响,高值区多分布在地势平坦、交通连通性较好、植被覆盖度高、有河流穿越的区域;低值区集中于岷山、米仓山、邛崃山、大凉山和高黎贡山等地形复杂地区。恢复力平均值高达0.667,西部和西北部因过度放牧引发草地退化、盐碱化和沙化等问题而呈低值,城镇发达、耕地密集和湖泊所在地也为低值区。生态系统健康分布呈西部、西北部、东部和东南部较低,东北部、中部和南部较高的格局。综合生态阻力面平均值为32.716,与生态系统健康分布趋势相反。生态安全格局共包含210块生态源地,面积66 990.64 km2,占总面积的28.28%;生态廊道511条,总长度达5 951.475 km;在空间分布上呈现出西部密集、东部稀疏的特征。一般生态廊道(250条)长且分散,连接较远生态源;重要生态廊道(178条)短而密集,与一般廊道形成廊道网络;核心生态廊道(83条)连接面积较大源地。共识别出143个生态夹点和248个生态障碍点,主要分布于一般生态廊道上,以草地、其他用地和耕地为主。结论: 本研究揭示出川滇生态屏障区生态系统物理健康的区域差异,生态系统健康整体呈南北高、东西低分布格局。东北部、中部和南部是生态源地和夹点的集中分布区,应优先保护自然植被的完整性;阿坝州、甘孜州和香格里拉地区受自然与人为活动的影响显著,应重点修复;应进一步优化东北部和南部地区的空间规划,协调生态与经济的可持续发展。
中图分类号:
刘娇,杨爱霞,李帅锋,苏建荣. 基于生态系统健康的川滇生态屏障区生态安全格局构建[J]. 林业科学, 2026, 62(1): 42-56.
Jiao Liu,Aixia Yang,Shuaifeng Li,Jianrong Su. Construction of Ecological Security Pattern in Sichuan-Yunnan Ecological Barrier Area Based on Ecosystem Health[J]. Scientia Silvae Sinicae, 2026, 62(1): 42-56.
表1
数据来源"
| 研究参数Research parameters | 年份Year | 空间分辨率Spatial resolution | 数据来源Data sources |
| 土地利用/覆盖Land use/land cover(LULC) | 2021 | 30 m | 中国科学院空天信息创新研究院Aerospace Information Research Institute, Chinese Academy of Sciences |
| 数字高程模型Digital elevation model | 2019 | 30 m | NASA地球科学数据NASA Earth Science Data( |
| 年均气温、逐月降水数据集、逐月潜在蒸散发数据集Annual mean temperature, Monthly precipitation dataset, Monthly potential evapotranspiration dataset | 2021 | 1 000 m | 国家青藏高原科学数据中心National Qinghai-Tibet Plateau Science Data Center (http://data.tpdc.ac.cn) |
| 土壤数据Soil data | 2010— 2018 | 90 m | 国家科技基础条件平台——国家地球系统科学数据中心National Earth System Science Data Center, National Science & Technology Infrastructure of China ( |
| 归一化植被指数Normalized vegetation index(NDVI) | 2021 | 30 m | 采用2021年Landsat遥感影像计算Calculated with Landsat remote sensing images in 2021 |
| 净初级生产力Net primary productivity(NPP) | 2021 | 500 m | MYD17A3HGF数据集MYD17A3HGF dataset ( |
| 道路、湖泊、河流数据Road, lake, and river data | 2021 | 矢量数据 Vector data | OpenStreetMap( |
表3
2021年每种土地利用类型的碳密度校正值"
| 土地利用类型 Land use type | 地上生 物量碳 Aboveground biomass carbon | 地下生 物量碳 Underground biomass carbon | 土壤有 机碳 Soil organic carbon | 死有 机碳 Dead organic matter carbon |
| 耕地Farmland | 0.411 1 | 2.734 1 | 93.437 7 | 0 |
| 林地Forest | 12.174 4 | 48.916 8 | 111.922 9 | 2.177 3 |
| 草地Grassland | 0.474 7 | 4.857 4 | 90.657 9 | 0.09 |
| 灌木地Shrubland | 4.662 7 | 5.828 4 | 89.205 | 0.924 2 |
| 水域Water | 0 | 0 | 0 | 0 |
| 建设用地Built-up land | 4.804 3 | 1.921 7 | 70.628 3 | 0 |
| 交通运输用地 Transportation land | 4.941 5 | 1.976 6 | 71.815 1 | 0 |
| 其他Other | 0 | 0 | 0 | 0 |
表4
不同风险情景下的权衡值与位序权重①"
| 情景Scenario | 风险Risk | 权衡Trae-off | w1 | w2 | w3 | w4 | w5 |
| 1 | 0 | 0 | 0.000 | 0.000 | 0.000 | 0.000 | 1.000 |
| 2 | 0.1 | 0.374 | 0.000 | 0.000 | 0.033 | 0.333 | 0.633 |
| 3 | 0.2 | 0.570 | 0.000 | 0.040 | 0.180 | 0.320 | 0.460 |
| 4 | 0.3 | 0.717 | 0.040 | 0.120 | 0.200 | 0.280 | 0.360 |
| 5 | 0.4 | 0.859 | 0.120 | 0.160 | 0.200 | 0.240 | 0.280 |
| 6 | 0.5 | 1.000 | 0.200 | 0.200 | 0.200 | 0.200 | 0.200 |
| 7 | 0.6 | 0.859 | 0.280 | 0.240 | 0.200 | 0.160 | 0.120 |
| 8 | 0.7 | 0.717 | 0.360 | 0.280 | 0.200 | 0.120 | 0.040 |
| 9 | 0.8 | 0.570 | 0.460 | 0.320 | 0.180 | 0.040 | 0.000 |
| 10 | 0.9 | 0.374 | 0.633 | 0.333 | 0.033 | 0.000 | 0.000 |
| 11 | 1 | 0 | 1.000 | 0.000 | 0.000 | 0.000 | 0.000 |
表5
生态阻力因素的权重和分级标准"
| 阻力因子Resistance factor | 权重 Weight | 相对阻力值Relative resistance value | ||||
| 10 | 30 | 50 | 70 | 90 | ||
| 土地发展概率因子 Land development probability factor | 0.416 7 | 基于公式(11)Calculation based on equation (11) | ||||
| 海拔Elevation/ m | 0.142 6 | <2 000 | 2 000–2 500 | 2 500–3 000 | 3 000–3 500 | >3 500 |
| 坡度Slope/ (°) | 0.056 7 | <8 | 8~15 | 15~25 | 25~35 | >35 |
| 地形起伏度Topographic relief/m | 0.074 5 | <100 | 100~200 | 200~300 | 300~400 | >400 |
| 植被覆盖度Vegetation coverage (%) | 0.158 8 | >0.8 | 0.6~0.8 | 0.4~0.6 | 0.2~0.4 | <0.2 |
| 距道路距离Distance from road/m | 0.083 3 | >5 000 | 2 000~5 000 | 1 000~2 000 | 500~1 000 | <500 |
| 土壤侵蚀量Amount of soil erosion/ (t·km?2) | 0.067 4 | <500 | 500~1 000 | 1 000~2 000 | 2 000~5 000 | >5 000 |
表6
不同情景下各生态系统服务的保护效率"
| 情景 Scenario | 生态系统物理健康Ecosystem physical health | 生态系统服务Ecosystem service | 平均保护效率 Average protection efficiency | ||||||
| 生态活力 Ecological vigor | 生态组织力 Ecological organization | 生态恢复力 Ecological resilience | 产水量 Water yield | 生境质量 指数Habitat quality index | 碳储量 Carbon storage | 土壤保持量 Soil retention capacity | |||
| 1 | 1.388 | 1.241 | 1.360 | 0.737 | 1.114 | 1.200 | 1.113 | 1.164 8 | |
| 2 | 1.371 | 1.246 | 1.359 | 0.780 | 1.134 | 1.201 | 1.153 | 1.177 6 | |
| 3 | 1.354 | 1.245 | 1.352 | 0.840 | 1.139 | 1.201 | 1.205 | 1.190 9 | |
| 4 | 1.338 | 1.243 | 1.346 | 0.895 | 1.141 | 1.200 | 1.231 | 1.199 2 | |
| 5 | 1.323 | 1.240 | 1.341 | 0.937 | 1.142 | 1.199 | 1.247 | 1.204 1 | |
| 6 | 1.300 | 1.231 | 1.333 | 0.995 | 1.144 | 1.197 | 1.270 | 1.209 9 | |
| 7 | 1.271 | 1.197 | 1.324 | 1.077 | 1.147 | 1.194 | 1.326 | 1.219 3 | |
| 8 | 1.234 | 1.130 | 1.310 | 1.181 | 1.148 | 1.189 | 1.410 | 1.228 7 | |
| 9 | 1.196 | 1.061 | 1.279 | 1.267 | 1.133 | 1.175 | 1.489 | 1.228 6 | |
| 10 | 1.177 | 1.028 | 1.224 | 1.293 | 1.100 | 1.148 | 1.498 | 1.209 7 | |
| 11 | 0.957 | 0.945 | 0.381 | 1.162 | 0.485 | 0.737 | 0.400 | 0.723 9 | |
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